Diversidad y control biológico de insectos - CyberTesis UACh ...
Diversidad y control biológico de insectos - CyberTesis UACh ... Diversidad y control biológico de insectos - CyberTesis UACh ...
within-field control plots as well as surrounding untreated fields (Thacker and Dixon, 1996; Huusela-Veistola, 1996; Duffield and Aebischer, 1994). Indeed, Jepson and Thacker (1990) demonstrated a significant positive correlation between the scale on which the experiment was carried out and the duration of the treatment effect. We raise concerns on spraying of broad spectrum insecticides such as lambda-cyhalothrin to control Dalaca sp. based in our findings because persistent negative effects were detected despite of small plot size and absence of barriers of movement. In addition, the 4 most abundant species are spring breeders and if egg-bearing females are removed from population, negative consequences for that local population could extent to the next generation. The predation on items used by adult in the current season and by the larvae in the summer and autumn could be relaxed, increasing the chance of herbivores outbreaks. This situation would be stressed if we consider that in practice, whole fields are treated and no control plots exist, therefore less migrant sources are available. While single predator taxa can, at times, have a strong impact on checking a target pest, there is growing evidence that diverse guilds may be more effective (Koss et al., 2005). This has been suggested for carabids (Symondson et al., 2002) as well as spiders (Greenstone, 1999; Sunderland, 1999). Therefore, we advocated for the conservation of the whole surface predator assemblage rather than a single species. Conclusions. The spring surface predator assemblage was make up mostly by carabids belonging to Ferionomorpha nebroides (Curtis), Allendia chilensis (Dejean), Argutoridius chilensis (Dejean) and Ferionomorpha aerea (Dejean). The spiders were represented equally by two families, Lycosidae and Gnaphosidae, differing from spider assemblages surveyed in other countries and agroecosystems. No species was affected by B. bassiana at the applied dose, despite of significant numbers of spores were present in soil (up to 15 days) and foliage (up to 7 days) and that B. bassiana isolate B-931 was able to kill at least one carabid species in laboratory (Devotto, unpub. data). This finding confirmed results from other field studies on mass-release of B. bassiana, which reported than negative effects on non target species are no existent or minimal (Lynch and Thomas, 2000). In contrast, the insecticide lambda-cyhalothrin affected at least two carabid species and the two spider families. The recovery times of 63
affected species, when present, where longer than those often reported in literature. Therefore, the use of this fungus would pose less risk to the generalist predators of Southern Chilean pastures than the synthetic pyrethroid used for D. pallens suppression. Acknowledgments. The authors thank specially to Leticia Silvestre, Universidad Austral de Chile, and Milenko Aguilera, Universidad de Concepción, Chile, for taxonomic guidance and identification. This research was funding by Dirección de Investigación y Desarrollo, Universidad Austral de Chile and MECESUP project AUS-9904. References. Alderweireldt, M., 1989. An ecological analysis of the spider fauna (Araneae) occurring in maize fields, Italian ryegrass fields and their edges zones, by means of different multivariate techniques. Agric. Ecosys. Environ. 27, 293-306. Allen, W.R., Hagley, E.A.C., 1989. Epigeal arthropods as predators of mature larvae and pupae of the apple maggot (Diptera: Tephritidae). Environ. Entomol. 19(2), 309-312. Banks, J.E., 2004. Divided culture: integrating agriculture and conservation biology. Front. Ecol. 2(10), 537-545. Bell, J.R., Wheater, C.P., Cullen, W.R., 2001. The implications of grassland and heathland management for the conservation of spider communities: a review. J. Zool. Lond. 255, 377-387. Bishop, L., Riechert, S.E., 1990. Spider colonization of agroecosystems: mode and source. Environ. Entomol. 19, 1738-1745. Clark, M.S., Luna J.M., Stone, N.D., Youngman, R.R., 1994. Generalist predator consumption of armyworm (Lepidoptera: Noctuidae) and effect of predator removal on damage in no-till corn. Environ. Entomol. 23, 617-622. Cole, L.J., McCracken, D.I., Dennis, P., Downie, I.S., Griffin, A.L., Foster, G.N., Murphy, K.J., Waterhouse, T., 2002. Relationships between agricultural management and ecological groups of ground beetles (Coleoptera: Carabidae) on Scottish farmland. Agric. Ecosys. Environ 93, 323-336. Dennis, P., Wratten, S.D., 1991. Field manipulation of populations of individual staphylinid species in cereals and their impact on aphid populations. Ecol. Entomol. 16, 17-24. 64
- Page 27 and 28: con la consiguiente pérdida o dism
- Page 29 and 30: 4. Numerosos estudios se concentran
- Page 31 and 32: 1.- CAPÍTULO PRIMERO: DIVERSIDAD G
- Page 33 and 34: sample, showing the potential use o
- Page 35 and 36: and put it in a phylogeographical p
- Page 37 and 38: centrifugation and supernatant was
- Page 39 and 40: (Schneider and Excoffier, 1999; Alt
- Page 41 and 42: All the putative populations showed
- Page 43 and 44: strongly influenced by insect host
- Page 45 and 46: supported a geographical sub-divisi
- Page 47 and 48: Neuveglise C, Brygoo Y, Vercrambe B
- Page 49 and 50: Table 1. Environmental data for the
- Page 51 and 52: B907 Poike 27º 06' 109º 21' Easte
- Page 53 and 54: B606 Lago Icalma 38º 50' 71º 20'
- Page 55 and 56: Figure 1. NJ tree of the B fragment
- Page 57 and 58: Figure 2. Haplotype tree inferred f
- Page 59 and 60: Figure 4. Mismatch distributions of
- Page 61 and 62: Figure 5. Haplotype diversity in th
- Page 63 and 64: Table 6. Analyses of molecular vari
- Page 65 and 66: Table 8. Pairwise differentiation e
- Page 67 and 68: CONSERVATION BIOLOGICAL CONTROL OF
- Page 69 and 70: Introduction. In last decades, mode
- Page 71 and 72: a dose of 10 12 spores per ha was s
- Page 73 and 74: aerea were very low at 1 and 30 day
- Page 75 and 76: explanation than no toxicity of the
- Page 77: fields that are sprayed with pestic
- Page 81 and 82: Kiss, B., Samu, F., 2000. Evaluatio
- Page 83 and 84: Wilby, A., Villareal, S., Lan, L.,
- Page 85 and 86: ARANEAE Gnaphosidae 253 54 % Lycosi
- Page 87 and 88: Activity density (individuals per p
- Page 89 and 90: NON-TARGET EFFECTS OF Dalaca pallen
- Page 91 and 92: same percentage of mortality on lar
- Page 93 and 94: Treatments were applied on 15 Octob
- Page 95 and 96: (Departamento de Producción y Sani
- Page 97 and 98: Predators. Data set I. The principa
- Page 99 and 100: predators extracted from soil cores
- Page 101 and 102: particularly carabids. Most of the
- Page 103 and 104: the consistent results allow us to
- Page 105 and 106: Kenmore, P.E., Cariño, F., Perez,
- Page 107 and 108: Traugott, M., Strasser, H. and Prie
- Page 109 and 110: Table 2. Significance of treatment
- Page 111 and 112: Figure 1. Persistence of B. bassian
- Page 113 and 114: Figure 3. Principal response curve
- Page 115 and 116: Figure 5. Principal response curve
- Page 117 and 118: RESPONSE OF GRASSLAND SOIL ARTHROPO
- Page 119 and 120: Introduction. Declining diversity h
- Page 121 and 122: Fungus. Beauveria bassiana strain Q
- Page 123 and 124: Data collection. The abundance and
- Page 125 and 126: N is the total number of individual
- Page 127 and 128: catches), while dominant species re
within-field <strong>control</strong> plots as well as surrounding untreated fields (Thacker and Dixon, 1996;<br />
Huusela-Veistola, 1996; Duffield and Aebischer, 1994). In<strong>de</strong>ed, Jepson and Thacker (1990)<br />
<strong>de</strong>monstrated a significant positive correlation between the scale on which the experiment<br />
was carried out and the duration of the treatment effect. We raise concerns on spraying of<br />
broad spectrum insectici<strong>de</strong>s such as lambda-cyhalothrin to <strong>control</strong> Dalaca sp. based in our<br />
findings because persistent negative effects were <strong>de</strong>tected <strong>de</strong>spite of small plot size and<br />
absence of barriers of movement. In addition, the 4 most abundant species are spring<br />
bree<strong>de</strong>rs and if egg-bearing females are removed from population, negative consequences<br />
for that local population could extent to the next generation. The predation on items used by<br />
adult in the current season and by the larvae in the summer and autumn could be relaxed,<br />
increasing the chance of herbivores outbreaks. This situation would be stressed if we<br />
consi<strong>de</strong>r that in practice, whole fields are treated and no <strong>control</strong> plots exist, therefore less<br />
migrant sources are available.<br />
While single predator taxa can, at times, have a strong impact on checking a target pest,<br />
there is growing evi<strong>de</strong>nce that diverse guilds may be more effective (Koss et al., 2005).<br />
This has been suggested for carabids (Symondson et al., 2002) as well as spi<strong>de</strong>rs<br />
(Greenstone, 1999; Sun<strong>de</strong>rland, 1999). Therefore, we advocated for the conservation of the<br />
whole surface predator assemblage rather than a single species.<br />
Conclusions.<br />
The spring surface predator assemblage was make up mostly by carabids belonging to<br />
Ferionomorpha nebroi<strong>de</strong>s (Curtis), Allendia chilensis (Dejean), Argutoridius chilensis<br />
(Dejean) and Ferionomorpha aerea (Dejean). The spi<strong>de</strong>rs were represented equally by two<br />
families, Lycosidae and Gnaphosidae, differing from spi<strong>de</strong>r assemblages surveyed in other<br />
countries and agroecosystems.<br />
No species was affected by B. bassiana at the applied dose, <strong>de</strong>spite of significant numbers<br />
of spores were present in soil (up to 15 days) and foliage (up to 7 days) and that B. bassiana<br />
isolate B-931 was able to kill at least one carabid species in laboratory (Devotto, unpub.<br />
data). This finding confirmed results from other field studies on mass-release of B.<br />
bassiana, which reported than negative effects on non target species are no existent or<br />
minimal (Lynch and Thomas, 2000). In contrast, the insectici<strong>de</strong> lambda-cyhalothrin<br />
affected at least two carabid species and the two spi<strong>de</strong>r families. The recovery times of<br />
63